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Why are urban stream buffers important? |
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Benefits of stream buffers |
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Performance criteria for stream buffers |
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Buffer planning considerations |
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Urban stream buffer zones |
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Buffer conflicts and opportunities |
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Buffer design and management |
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Customizing buffer criteria for unique goals and
constraints |
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Documented decline in riparian cover with
increased impervious surface in a watershed |
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Documented decline in index of biotic integrity scores
with increased impervious surface |
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Provide habitat and runoff filtering |
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90% of buffers in private ownership |
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90% had a neutral or positive impact on property
values |
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26% indicated buffers often impaired during
construction |
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Buffer Programs... |
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30% had significant complaints |
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25% recently strengthened |
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48% had “weak” or no notification methods |
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50% required delineation of buffers on grading/
E&S plans |
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67% did not record buffers on any official map |
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60% of property owners unaware of boundaries/
uses |
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Few make forests the vegetative target
(predevelopment cover or no target at all) |
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Allows streams to move laterally over time |
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Prerequisite for future stream restoration
projects |
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Reduces watershed imperviousness |
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Reduces small drainage complaints |
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Most effective flood control insurance |
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Allows for forest conservation/reforestation
sites |
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Serves as foundation for greenway system |
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Discourages storm drain enclosures |
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Provides sites for stormwater detention ponds |
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Minimizes creation of new fish barriers |
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Provides a separation distance from impervious
cover |
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Provides additional streambank erosion
protection |
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Can help increase property values |
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Provides food and riparian habitat for wildlife |
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Provides fish and wildlife migration corridors |
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Helps mitigate stream warming |
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Helps promote associated wetland protection |
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Increases pollutant removal? |
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Helps prevent steep slope disturbance |
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Flash floods kill about 40 people per year |
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About 45% of deaths involve cars |
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Flash floods cause about a billion dollars of
property damage per year |
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40% of the flood damage is reported to be
outside of the mapped floodplain |
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Source: FEMA, NOAA |
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A setback is not a buffer |
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The floodplain is the core of the buffer |
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Management is as important as width |
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Model Ordinances are available on the internet: |
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www.cwp.org |
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www.stormwatercenter.net |
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More detail on buffer programs and strategies is
available in The Practice of Watershed Protection available at www.cwp.org |
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See articles 39 to 44 |
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Urban stream warming from 5 to 15 degrees is
caused by a variety of factors: |
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Impervious surfaces |
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Stormwater ponds |
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Stream channel hardening |
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Loss of riparian cover |
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An 80% riparian forest cover provides cooling |
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A 60% riparian forest cover prevents warming |
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Runoff volumes can greatly increase from
predevelopment conditions |
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Stream channel and floodplain geometry may be
out of equilibrium |
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Even 2-year stormwater management can exacerbate
streambank erosion |
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Runoff is delivered to a stream in one of four
ways: |
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Open channels |
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Stormdrain pipes |
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Swales |
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BMP outfalls |
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Stream buffers DO NOT typically remove
pollutants in urban stormwater |
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Buffers are poorly integrated with stormwater BMPs |
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Stream corridors experience heavy use and
encroachment |
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Stream buffers remain as private property |
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Many property owners are unaware of buffers
existence |
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Buffers are not well protected during
construction |
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Little reliable monitoring data exists |
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Removal rates for agricultural systems are not
transferable |
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Concentrated stormwater flows often bypass
buffer |
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Need to “engineer” outer buffer boundary |
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Septic system setback requirements are important |
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Stream buffers are more than a line on a map |
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1st and 2nd order streams comprise 75% of total
stream and river mileage |
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Effective stream protection requires strong
local ordinances |
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10 performance criteria exist for local
ordinances |
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Stream buffer width |
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Three zone urban stream buffers |
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Predevelopment vegetative target for stream
buffers |
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Stream buffer expansion and contraction |
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Stream buffer delineation |
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Stream buffer crossings |
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Use of buffers for stormwater treatment and
siting BMPs |
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Stream buffer plan review considerations |
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Post-development management of the stream buffer |
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Protecting property rights within stream buffers |
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Range: 20 to 200 feet |
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Recommended base width 100 feet |
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Special protection areas 150 feet (trout,
septic systems,
shorelines) |
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Benefits include pollutant removal, flood
insurance, wildlife habitat, shading, streambank protection, fish passage,
access, and higher property values |
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Each zone has different function, width,
vegetative target, and management: |
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Streamside zone: 25 feet of undisturbed
forest cover |
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Middle zone: 50 feet or more of
managed forest |
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Outer zone: 25 feet of grass or forest
setback from structures |
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Many buffer benefits are amplified by forest
cover |
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Target is mature predevelopment riparian plant
community |
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Determined from undisturbed “reference”
floodplain plant communities |
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Turfgrass allowed in outer zone |
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May require succession or reforestation in
streamside/middle zones |
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Base width may be expanded to include: |
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Ultimate 100 year floodplain |
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Any steep slopes greater than 25% |
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Four feet per 1% increase in slope over 5% |
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Delineated wetlands, critical habitats, forest
conservation |
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25 feet more for 3rd and 4th order streams |
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50 feet for fifth order rivers |
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Start with USGS 7.5 minute quad map - all
“blueline” streams at a minimum |
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However, these do not reveal all first order
streams or their exact origin |
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Field delineation: |
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Distinct channel with unvegetated streambed and
high water marks, or |
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Upper limit of running water in wet season |
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Inner edge of buffer may be stream centerline or
bank depending on stream order |
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The number and kind of stream buffer crossings
are clearly defined |
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Create an unbroken corridor that supports fish
passage |
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Width: minimum right of way needed for
access |
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Angle: perpendicular to stream |
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Frequency: no more than one crossing/1000
feet |
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Depth: utilities three feet below
streambed |
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Capacity: convey ultimate 100 year storm |
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Culverts: bottomless, slab, arch or box
designs preferred |
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The stream buffer is one element of the total
stormwater treatment system for the watershed |
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Locating structural BMPs (e.g. large ponds and
wetlands) in buffers should be restricted to: |
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No more than 100 acres contributing drainage, or |
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Within the first 500 feet of a perennial stream |
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Off-line location in middle or outer zone |
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Urban stream buffers can provide limited
filtering of stormwater: |
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Up to 75 feet of adjacent impervious areas |
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Up to 150 feet of adjacent pervious areas
(including rooftops) |
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Pollutant removal frequently cited as
justification for urban stream buffers (61% of local governments) |
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Little evidence that buffers actually remove
urban pollutants in stormwater |
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Best performance is for systems with level
spreader and 150 feet of mowed grass (Yu et. al, 1990) |
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Most sites will require a BMP for long-term
pollutant removal |
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Small structural BMPs need to be carefully
integrated into buffer system |
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BMP TSS TP Zinc Lead |
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Grass channels 81 40 71 67 |
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Filter Strip - 75’ 54 -25 47 -16 |
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Filter Strip - 150’ 84 40 55 50 |
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Mean Non-Urban 73 56 NA NA |
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Buffer boundaries & uses must be clearly
defined: |
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Delineate on preliminary and final plans |
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Verify stream delineation in field |
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Check for expansions, crossings, &
stormwater treatment |
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Mark boundaries on all |
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construction plans |
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Preconstruction |
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walk-through |
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Fencing of boundaries |
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Maintain visibility of buffer after development: |
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Mark boundaries |
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Educate landowners about boundaries and benefits |
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Clear notification upon resale |
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Bufferscaping programs |
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Annual buffer walks to check for encroachment |
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Intent is to change the location of development
within a parcel, not its density.
Local governments may wish to use some of these tools: |
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Maintaining buffers in private ownership |
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Buffer averaging |
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Fair and timely administrative appeals |
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Conservation easements and property tax |
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reduction |
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Stormwater management volume credits |
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Example: |
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Parcel size: 10 ac |
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Housing density: 2 du/ac |
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Estimated number of homes: 20 |
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% parcel delineated as buffer: 15% |
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Density credit: 1.1 |
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Buildable parcel size = (10 ac) (85%) = 8.5 ac |
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Adjusted housing density = (2 du/ac) (1.1) = 2.2
du/ac |
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Adjusted number of homes = (8.5 ac) (2.2 du/ac)
= approximately 19 homes (18.7) |
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While 80% of buffer programs report strong
public support, there are some resident concerns: |
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Access |
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Illegal uses and policing |
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Obstruct water view |
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Taxed on land they cannot utilize |
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Need for composting/firewood |
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Varmints/weeds/ticks |
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How much of the aquatic corridor can be
protected by buffers? |
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How should buffers be managed & crossed? |
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What kinds of water dependent uses can be
restricted? |
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Should public access be restricted to designated
areas? |
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Is restoration or better stewardship possible
along an aquatic corridor that has already been developed? |
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How will the buffer network be managed? |
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Long-term maintenance? |
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How much pollutant removal is to be expected? |
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Buffers must be adapted for local watershed
management objectives: |
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Lake shorelines |
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Greenways |
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Impacted/non supporting streams |
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Reservoir protection |
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Arid and semi-arid climates |
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Flat and steep terrains |
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Rural land uses |
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Septic versus sewer |
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Buffers can be implemented various ways to
protect riparian stream corridors, lakes and coastal areas. |
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Buffers are typically a low-cost means for
meeting some stormwater management goals, improving water quality, and
providing habitat. |
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Buffers provide flood hazard mitigation and
physical separation distance between humans and waters. |
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Buffers can be adapted to various development,
political and physical landscapes. |
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